CN105498707B - A kind of preparation method and application of modified graphene oxide/Chitosan Composites - Google Patents
A kind of preparation method and application of modified graphene oxide/Chitosan Composites Download PDFInfo
- Publication number
- CN105498707B CN105498707B CN201510915633.XA CN201510915633A CN105498707B CN 105498707 B CN105498707 B CN 105498707B CN 201510915633 A CN201510915633 A CN 201510915633A CN 105498707 B CN105498707 B CN 105498707B
- Authority
- CN
- China
- Prior art keywords
- graphene oxide
- chitosan
- preparation
- modified graphene
- modified
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Fee Related
Links
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical class [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 title claims abstract description 112
- 229920001661 Chitosan Polymers 0.000 title claims abstract description 99
- 239000002131 composite material Substances 0.000 title claims abstract description 55
- 238000002360 preparation method Methods 0.000 title claims abstract description 27
- 229910021389 graphene Inorganic materials 0.000 claims abstract description 50
- 239000000725 suspension Substances 0.000 claims abstract description 35
- 238000003756 stirring Methods 0.000 claims abstract description 30
- QTBSBXVTEAMEQO-UHFFFAOYSA-N Acetic acid Chemical compound CC(O)=O QTBSBXVTEAMEQO-UHFFFAOYSA-N 0.000 claims abstract description 27
- 239000003463 adsorbent Substances 0.000 claims abstract description 26
- 239000002351 wastewater Substances 0.000 claims abstract description 17
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 14
- 229960000583 acetic acid Drugs 0.000 claims abstract description 13
- 239000003109 Disodium ethylene diamine tetraacetate Substances 0.000 claims abstract description 12
- 235000019301 disodium ethylene diamine tetraacetate Nutrition 0.000 claims abstract description 12
- 239000012362 glacial acetic acid Substances 0.000 claims abstract description 12
- 229910001385 heavy metal Inorganic materials 0.000 claims abstract description 8
- 239000000463 material Substances 0.000 claims abstract description 8
- 238000005119 centrifugation Methods 0.000 claims abstract description 3
- 238000000967 suction filtration Methods 0.000 claims abstract description 3
- 238000009210 therapy by ultrasound Methods 0.000 claims abstract description 3
- ZGTMUACCHSMWAC-UHFFFAOYSA-L EDTA disodium salt (anhydrous) Chemical compound [Na+].[Na+].OC(=O)CN(CC([O-])=O)CCN(CC(O)=O)CC([O-])=O ZGTMUACCHSMWAC-UHFFFAOYSA-L 0.000 claims abstract 5
- 239000000243 solution Substances 0.000 claims description 40
- JOPOVCBBYLSVDA-UHFFFAOYSA-N chromium(6+) Chemical compound [Cr+6] JOPOVCBBYLSVDA-UHFFFAOYSA-N 0.000 claims description 23
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 12
- 239000011259 mixed solution Substances 0.000 claims description 11
- 238000004090 dissolution Methods 0.000 claims description 9
- 229910002804 graphite Inorganic materials 0.000 claims description 9
- 239000010439 graphite Substances 0.000 claims description 9
- BDOYKFSQFYNPKF-UHFFFAOYSA-N 2-[2-[bis(carboxymethyl)amino]ethyl-(carboxymethyl)amino]acetic acid;sodium Chemical compound [Na].[Na].OC(=O)CN(CC(O)=O)CCN(CC(O)=O)CC(O)=O BDOYKFSQFYNPKF-UHFFFAOYSA-N 0.000 claims description 7
- 125000002887 hydroxy group Chemical group [H]O* 0.000 claims description 7
- 238000006243 chemical reaction Methods 0.000 claims description 6
- 238000001291 vacuum drying Methods 0.000 claims description 6
- 238000003795 desorption Methods 0.000 claims description 5
- 238000010521 absorption reaction Methods 0.000 claims description 4
- 238000013019 agitation Methods 0.000 claims description 4
- 125000002924 primary amino group Chemical group [H]N([H])* 0.000 claims description 4
- 230000009471 action Effects 0.000 claims description 3
- 125000003178 carboxy group Chemical group [H]OC(*)=O 0.000 claims description 3
- 230000002045 lasting effect Effects 0.000 claims description 3
- 238000012545 processing Methods 0.000 claims description 3
- QXNVGIXVLWOKEQ-UHFFFAOYSA-N Disodium Chemical compound [Na][Na] QXNVGIXVLWOKEQ-UHFFFAOYSA-N 0.000 claims description 2
- PIICEJLVQHRZGT-UHFFFAOYSA-N Ethylenediamine Chemical compound NCCN PIICEJLVQHRZGT-UHFFFAOYSA-N 0.000 claims description 2
- 150000001336 alkenes Chemical class 0.000 claims description 2
- 125000003277 amino group Chemical group 0.000 claims description 2
- ZCDOYSPFYFSLEW-UHFFFAOYSA-N chromate(2-) Chemical compound [O-][Cr]([O-])(=O)=O ZCDOYSPFYFSLEW-UHFFFAOYSA-N 0.000 claims description 2
- 230000009881 electrostatic interaction Effects 0.000 claims description 2
- 238000000527 sonication Methods 0.000 claims description 2
- 238000001179 sorption measurement Methods 0.000 abstract description 25
- 230000008901 benefit Effects 0.000 abstract description 6
- 239000000203 mixture Substances 0.000 abstract description 6
- 238000003911 water pollution Methods 0.000 abstract description 4
- 239000002994 raw material Substances 0.000 abstract description 2
- 239000004615 ingredient Substances 0.000 abstract 1
- 238000000034 method Methods 0.000 description 22
- KCXVZYZYPLLWCC-UHFFFAOYSA-N EDTA Chemical compound OC(=O)CN(CC(O)=O)CCN(CC(O)=O)CC(O)=O KCXVZYZYPLLWCC-UHFFFAOYSA-N 0.000 description 10
- 239000008367 deionised water Substances 0.000 description 9
- 229910021641 deionized water Inorganic materials 0.000 description 9
- 238000002156 mixing Methods 0.000 description 8
- 230000008569 process Effects 0.000 description 8
- 238000010586 diagram Methods 0.000 description 7
- 239000011651 chromium Substances 0.000 description 6
- 239000011521 glass Substances 0.000 description 6
- 239000000047 product Substances 0.000 description 6
- 238000005303 weighing Methods 0.000 description 6
- 239000007788 liquid Substances 0.000 description 5
- 239000012528 membrane Substances 0.000 description 5
- 238000012360 testing method Methods 0.000 description 5
- 238000005406 washing Methods 0.000 description 5
- 229910001430 chromium ion Inorganic materials 0.000 description 4
- 238000002604 ultrasonography Methods 0.000 description 4
- 239000007864 aqueous solution Substances 0.000 description 3
- 239000013078 crystal Substances 0.000 description 3
- 238000001035 drying Methods 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 238000001914 filtration Methods 0.000 description 3
- 150000004676 glycans Chemical class 0.000 description 3
- 238000000227 grinding Methods 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 230000003647 oxidation Effects 0.000 description 3
- 238000007254 oxidation reaction Methods 0.000 description 3
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 2
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 description 2
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 2
- 239000002253 acid Substances 0.000 description 2
- 239000003929 acidic solution Substances 0.000 description 2
- 238000004458 analytical method Methods 0.000 description 2
- 229910052799 carbon Inorganic materials 0.000 description 2
- 239000003795 chemical substances by application Substances 0.000 description 2
- 150000001875 compounds Chemical class 0.000 description 2
- 238000002050 diffraction method Methods 0.000 description 2
- 229960001484 edetic acid Drugs 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 239000003344 environmental pollutant Substances 0.000 description 2
- 238000002474 experimental method Methods 0.000 description 2
- -1 graphite alkene Chemical class 0.000 description 2
- 238000002329 infrared spectrum Methods 0.000 description 2
- 150000002500 ions Chemical class 0.000 description 2
- 231100000719 pollutant Toxicity 0.000 description 2
- 229920001282 polysaccharide Polymers 0.000 description 2
- 239000005017 polysaccharide Substances 0.000 description 2
- 238000004064 recycling Methods 0.000 description 2
- 230000008929 regeneration Effects 0.000 description 2
- 238000011069 regeneration method Methods 0.000 description 2
- 230000004044 response Effects 0.000 description 2
- 229910052708 sodium Inorganic materials 0.000 description 2
- 239000011734 sodium Substances 0.000 description 2
- VWDWKYIASSYTQR-UHFFFAOYSA-N sodium nitrate Chemical compound [Na+].[O-][N+]([O-])=O VWDWKYIASSYTQR-UHFFFAOYSA-N 0.000 description 2
- 206010007269 Carcinogenicity Diseases 0.000 description 1
- XFXPMWWXUTWYJX-UHFFFAOYSA-N Cyanide Chemical compound N#[C-] XFXPMWWXUTWYJX-UHFFFAOYSA-N 0.000 description 1
- 206010013786 Dry skin Diseases 0.000 description 1
- 241001411320 Eriogonum inflatum Species 0.000 description 1
- 238000005033 Fourier transform infrared spectroscopy Methods 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 1
- 238000002441 X-ray diffraction Methods 0.000 description 1
- 239000002250 absorbent Substances 0.000 description 1
- 230000002745 absorbent Effects 0.000 description 1
- 239000002156 adsorbate Substances 0.000 description 1
- 239000002154 agricultural waste Substances 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 230000005540 biological transmission Effects 0.000 description 1
- 230000007670 carcinogenicity Effects 0.000 description 1
- 231100000260 carcinogenicity Toxicity 0.000 description 1
- 239000011248 coating agent Substances 0.000 description 1
- 238000000576 coating method Methods 0.000 description 1
- 230000009514 concussion Effects 0.000 description 1
- 239000000356 contaminant Substances 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 230000018109 developmental process Effects 0.000 description 1
- 238000000502 dialysis Methods 0.000 description 1
- 230000009977 dual effect Effects 0.000 description 1
- 230000005611 electricity Effects 0.000 description 1
- 238000004070 electrodeposition Methods 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 239000000706 filtrate Substances 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- 239000008236 heating water Substances 0.000 description 1
- 231100000086 high toxicity Toxicity 0.000 description 1
- 229910052739 hydrogen Inorganic materials 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- 239000005457 ice water Substances 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 238000005342 ion exchange Methods 0.000 description 1
- 238000011031 large-scale manufacturing process Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 239000002086 nanomaterial Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 230000020477 pH reduction Effects 0.000 description 1
- 239000000049 pigment Substances 0.000 description 1
- 238000007747 plating Methods 0.000 description 1
- 239000012286 potassium permanganate Substances 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 230000002441 reversible effect Effects 0.000 description 1
- 239000004317 sodium nitrate Substances 0.000 description 1
- 235000010344 sodium nitrate Nutrition 0.000 description 1
- 238000002336 sorption--desorption measurement Methods 0.000 description 1
- 239000004575 stone Substances 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-N sulfuric acid Substances OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 1
- 229910021653 sulphate ion Inorganic materials 0.000 description 1
- 230000002459 sustained effect Effects 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
- 239000003643 water by type Substances 0.000 description 1
- 239000002023 wood Substances 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/22—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
- B01J20/24—Naturally occurring macromolecular compounds, e.g. humic acids or their derivatives
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/20—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising free carbon; comprising carbon obtained by carbonising processes
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/22—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
- B01J20/223—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material containing metals, e.g. organo-metallic compounds, coordination complexes
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/288—Treatment of water, waste water, or sewage by sorption using composite sorbents, e.g. coated, impregnated, multi-layered
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J2220/00—Aspects relating to sorbent materials
- B01J2220/40—Aspects relating to the composition of sorbent or filter aid materials
- B01J2220/46—Materials comprising a mixture of inorganic and organic materials
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Analytical Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Inorganic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Carbon And Carbon Compounds (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Abstract
The invention discloses a kind of preparation method and applications of modified graphene oxide/Chitosan Composites.Modified composite ingredient includes graphene oxide, chitosan and disodium ethylene diamine tetraacetate.Preparation method are as follows: stir the disodium ethylene diamine tetraacetate for being dissolved in water in the graphene oxide suspension for being added and obtaining after ultrasonic treatment, mix it uniformly, it is subsequently agitated for that the chitosan solution being dissolved in glacial acetic acid is added, is stirred by ultrasonic after a period of time through suction filtration, centrifugation, is dried in vacuo and obtains modified graphene oxide/Chitosan Composites after being ground up, sieved.The modified material of preparation is used for field of water pollution control as adsorbent, the especially Adsorption of heavy metal pollution in wastewater object, have many advantages, such as that preparation method is easy, adsorption rate is fast, regenerability is good, and required raw material sources are extensive, at low cost, practical application value is high.
Description
Technical field
The present invention relates to technical field of water pollution control, and in particular to a kind of modified graphene oxide/chitosan composite wood
The preparation method and application of material.
Background technique
With the especially rapid development of developing country in the world of human society and industrial economy, cause therewith
Environmental problem very big risk and threat are brought to human health and public's environment, wherein heavy metal pollution of water body is not allowed small
It looks.China is used as a developing country, and industrial manufacturing industry is numerous, and the environmental problem thus caused also continuously emerges.Its
In, it is common in industrial wastewater for being widely used in the Cr VI of the industries such as intermetallic composite coating, process hides, plating and pigment manufacture
A kind of carcinogenicity heavy metal contaminants have very high toxicity, refractory organics and enriching, and therefore, Cr VI controls in waste water
Reason becomes one of the hot spot of social concerns.The method administered for Cr VI has very much, including at electrochemical deposition method, cyanide
Reason, ion exchange, redox, UF membrane etc., and absorption method relative to other methods and have speech expense it is low, it is easily operated,
The advantages such as effect is good, recyclable heavy metal, adsorbent are renewable, therefore become common method.Currently, a large amount of material is reported
Road is used to adsorb the Cr VI, such as active carbon, large biological molecule, agricultural wastes etc. in waste water.Although some adsorbent materials
Good adsorption effect is shown, but the reusable rate of these materials is relatively low, this will certainly result in waste of resources, increase
Add operating cost, and it is possible to secondary pollution can be brought.Graphene is a kind of two-dimension nano materials risen nearly ten years,
Huge specific surface area becomes a kind of adsorbent of good performance.But during the preparation process, graphene platelet can occur not
It is reversible to stack again, so that it is lost most specific surface area, to limit graphene as adsorbent in water pollution
Application in control.Chitosan contains a large amount of adsorption group amino and hydroxyl, often since its is cheap and easy to get in molecular structure
It is used for wastewater treatment as a kind of biological adsorption agent, but chitosan to be soluble in an acidic solution, in practical applications stability
It is bad, therefore also limit practical application of the chitosan in water pollution processing.
Summary of the invention
It is an object of the present invention to the removal for Pollutants in Wastewater provide it is a kind of it is economical, environmentally friendly, easily prepared, can
The modified graphene oxide of high recycling rate/Chitosan Composites adsorbent.
The second object of the present invention is to provide the preparation method of above-mentioned modified graphene oxide/Chitosan Composites,
This method simple process, equipment requirement are low, are easy to large-scale production.
The third object of the present invention is that provide above-mentioned modified graphene oxide/Chitosan Composites exists as adsorbent
Remove the application of hexavalent chromium in waste water.
The technical solution used in the present invention is as follows.
A kind of preparation method of modified graphene oxide/Chitosan Composites will be dissolved in the ethylenediamine tetra-acetic acid two of water
Sodium stirring is added in the graphene oxide suspension obtained after ultrasonic treatment, mixes it uniformly, is subsequently agitated for addition and is dissolved in
Chitosan solution in glacial acetic acid, ultrasonic agitation, after lasting electric stirring, through suction filtration, centrifugation, is dried in vacuo and is ground up, sieved
After obtain modified graphene oxide/Chitosan Composites.
The above method the following steps are included:
(1) graphene oxide suspension is obtained by graphite oxide suspension is sonicated；
(2) disodium ethylene diamine tetra-acetic acid solution is stirred and is added in graphene oxide suspension obtained in step (1), stirred
Mix mixing；
(3) chitosan is dissolved in glacial acetic acid, stirring is added in the mixed solution of step (2) after completely dissolution, and ultrasound is stirred
Uniform and stable suspension is persistently stirred to get after mixing；
(4) it is obtained after the suspension in step (3) being filtered, be centrifuged, be dried in vacuo and be ground up, sieved modified oxidized
Graphene/Chitosan Composites.
In the above method, sonication treatment time described in step (1) be 1h ~ 3h, the graphene oxide suspension it is dense
Degree is the mg/mL of 2.5mg/mL ~ 5.
In the above method, in step (2), the concentration of the edta solution is 15g/L ~ 25g/L, and stirring is mixed
The time of conjunction is the h of 4h ~ 6.
In the above method, in step (3), time of the ultrasonic agitation is 30min-60min, and the time persistently stirred is
14h~18 h；The glacial acetic acid solution concentration of the chitosan dissolution is 1% ~ 4%, the graphene oxide, ethylenediamine tetra-acetic acid two
The mass ratio of sodium and chitosan is 1:5 ~ 10:5 ~ 10.
In the above method, the preparation of modified graphene oxide/Chitosan Composites carries out at room temperature, vacuum drying
Temperature be 50 DEG C ~ 80 DEG C.
A kind of modified graphene oxide/Chitosan Composites, the modified graphene oxide/Chitosan Composites packet
Containing graphene oxide, disodium ethylene diamine tetraacetate and chitosan.
Further, the disodium ethylene diamine tetraacetate passes through the carboxylic-bond on amino group and graphene oxide, shell
Glycan is by carboxyl on its amino and hydroxyl and graphene oxide and hydroxyl generates bonding action and electrostatic interaction is incorporated in one
It rises.
A kind of modified graphene oxide/Chitosan Composites are applied to the processing of heavy metal-containing waste water as adsorbent.
Hexavalent chromium in above-mentioned application, in the removal heavy metal-containing waste water, the specific steps are as follows:
0.2 ~ 3.0 g of modified graphene oxide/Chitosan Composites is added in every liter of chromate waste water, and control waste water temperature is
It 25 ~ 45 DEG C, fullys shake to fully reacting, adsorbent material is separated with waste water, with the sodium hydroxide solution of 1 mol/L to suction
The adsorbent of attached saturation is desorbed, and control reaction temperature is 25 DEG C, is fullyd shake, and adsorbent is recycled benefit after desorption is complete
With.
Compared with prior art, the advantages of the present invention:
(1) present invention takes full advantage of the physicochemical characteristics of graphene oxide and chitosan, passes through ethylenediamine tetra-acetic acid
Disodium modification is compound by the two, drastically reduces the reunion of graphene oxide, also enhances chitosan in an acidic solution
Stability, while a large amount of adsorption groups are increased, and then improve composite material to the absorption property of pollutant；
(2) raw material rich reserves, cheap needed for the present invention, and not can cause environmental pollution in use,
Biggish economic benefit can be obtained with lower investment；
(3) material preparation process of the invention is simple and easy, equipment requirement is low, it is easy to accomplish large-scale serial production；
(4) modified graphene oxide/Chitosan Composites prepared by the present invention can quickly, efficiently as adsorbent
Hexavalent chromium in ground Adsorption waste water can use simple method desorption and regeneration after the adsorbent adsorption saturation, realize
The dual recycling of adsorbent and adsorbate, will not only bring secondary pollution, but also greatly reduce being processed into for waste water
This.
Detailed description of the invention
Fig. 1 is the scanning electron microscope (SEM) photograph of chitosan.
Fig. 2 is modified graphene oxide/Chitosan Composites scanning electron microscope (SEM) photograph prepared by the embodiment of the present invention 1.
Fig. 3 is modified graphene oxide/Chitosan Composites transmission electron microscope picture prepared by example 1 of the invention.
Fig. 4 is graphene oxide (GO), chitosan (CS), graphene oxide/chitosan (GC) and example 1 of the invention are made
The Fourier transform infrared contrast schematic diagram of standby modified graphene oxide/chitosan (GEC) adsorbent.
Fig. 5 is modified graphene oxide/shell prepared by chitosan, graphene oxide/chitosan and the embodiment of the present invention 1
The X-ray diffraction contrast schematic diagram of polysaccharide composite material.
Fig. 6 is modified graphene oxide/Chitosan Composites prepared by the embodiment of the present invention 1 and chitosan, oxidation
Graphene/chitosan is under differential responses time conditions to the adsorbance contrast schematic diagram of hexavalent chromium.
Fig. 7 is modified graphene oxide/Chitosan Composites prepared by the embodiment of the present invention 1 and chitosan, oxidation
Graphene/chitosan is under condition of different pH to the adsorbance contrast schematic diagram of hexavalent chromium.
Fig. 8 is modified graphene oxide/Chitosan Composites of the preparation of the embodiment of the present invention 1 in different dosages
Under the conditions of to the adsorbance contrast schematic diagram of hexavalent chromium.
Fig. 9 is absorption etc. of the modified graphene oxide/chitosan absorbent of the preparation of the embodiment of the present invention 1 to Cr VI
Warm line schematic diagram.
Figure 10 is that modified graphene oxide/Chitosan Composites prepared by the embodiment of the present invention 1 are de- in 7 wheel absorption-
To the adsorbance of hexavalent chromium and removal rate schematic diagram in attached experiment.
Specific embodiment
Below with reference to embodiment, the present invention will be further described.
Embodiment 1
(1) graphite oxide suspension is ultrasonically treated 2 h, obtains the graphene oxide that concentration is 2.5 mg/mL and suspends
Liquid；
Hummers method preparation of the graphite oxide suspension using improvement in the present embodiment, specific steps are as follows: by 120 ml
The concentrated sulfuric acid is added 1 L beaker and is placed in ice-water bath, is slowly stirred with electric mixer to it, when its temperature is down to 4 DEG C
When left and right, 5 g graphite and 2.5 g sodium nitrate are added, continues to be slowly added to 15 g potassium permanganate after stirring 1h, keep in the process
The temperature of reaction system is not higher than 10 DEG C, sustained response 3h；Beaker is moved in 35 DEG C of thermostat water bath, to system temperature liter
When to 35 DEG C, continue to be stirred to react 15h；230 ml deionized waters are persistently slowly added into beaker, control system temperature exists
98 DEG C hereinafter, heating water bath keeps system temperature at 90 DEG C or so, 30 ml are added into beaker after the reaction was continued 30 min
The hydrogen peroxide of 30 ﹪.Continue stirring until there is no bubble generations in system.Products therefrom is filtered by vacuum, is used in combination
The hydrochloric acid solution washing of 5 ﹪ until no longer sulphate-containing ion in filtrate, then with suitable deionized water to product carry out from
The heart is washed to its pH and is in neutrality, and product was finally obtained graphite oxide suspension with deionized water dialysis one week；
(2) disodium ethylene diamine tetra-acetic acid solution is stirred and is added in the graphene oxide suspension that step (1) obtains, stirred
Mix mixing；
Mixed solution the preparation method comprises the following steps: weighing 5g disodium ethylene diamine tetraacetate crystal in 250 ml beakers in the present embodiment
In, stirring after 250 ml of deionized water makes it dissolve is added and is added in the graphene oxide suspension in step (1), continues electronic
Stir 4h；
(3) chitosan is dissolved in glacial acetic acid, stirring is added in the mixed solution of step (2) after completely dissolution, and ultrasound is stirred
It mixes, rear lasting stirring obtains uniform and stable suspension；
Suspension is placed in the glacial acetic acid of 100mL2% the preparation method comprises the following steps: weighing 2.5g chitosan in the present embodiment, is used
Glass plate stirring stirs it after completely dissolution in the mixed solution of addition step (2), continues electric mixing after 40min is stirred by ultrasonic
Mix 16h；
(4) suspension in step (3) is obtained into brown product with deionized water filtering and washing afterwards for several times, is placed in vacuum
Drying to constant weight, grinding, 200 meshes excessively obtains modified graphene oxide/Chitosan Composites at 60 DEG C in drying
(GEC)。
Modified graphene oxide/Chitosan Composites microstructure that the present embodiment obtains is as shown in Fig. 2, and Fig. 1
Middle chitosan is compared, modified graphene oxide/Chitosan Composites surface in Fig. 2 want it is smooth very much, this is because oxygen
The composite modified dispersibility for improving the two of graphite alkene and chitosan.Can also see pure and freshly from Fig. 2 chitosan and
Graphene oxide is relatively uniformly dispersed throughout together.
It can be concluded that graphene oxide manufactured in the present embodiment has characteristic peak: 1086 cm in Fig. 4-1(C-O)、
1636 cm-1(C=C)、1727 cm-1(C=O)、3437 cm-1(O-H), it was demonstrated that graphene oxide is successfully prepared.The spy of chitosan
Levy peak: 1416cm-1(C-H)、1559cm-1(-NH2)、1646cm-1(-NHCO-)、3441cm-1(N-H).Modified graphene oxide/
1646cm in chitosan-1The peak of (- NHCO-) is enhanced compared to chitosan, illustrates the carboxyl and chitosan on graphene oxide
On amino react, generation-NHCO-.3437 cm of simultaneous oxidation graphene-1(O-H) peak shifts, and illustrates to aoxidize
Hydroxyl on hydroxyl and chitosan on graphene generates hydrogen bond action.
The diffraction maximum of chitosan appears in 20.3 ° in Fig. 5, and the characteristic diffraction peak of graphene oxide appears in 10.8 °, Fig. 5
Diffraction maximum of the middle GC at 20.3 ° is weaker than chitosan, occurs new diffraction maximum at 10.8 °, it was demonstrated that graphene oxide and chitosan
Success it is compound, and in Fig. 5 diffraction maximum of the GEC at 20.3 ° and 10.8 ° all it is weaker than GC very much, illustrate modifying agent ethylenediamine tetrem
Acid disodium takes part in reaction, has achieved the purpose that modified.
Embodiment 2
(1) graphite oxide suspension is ultrasonically treated 2 h, obtains the graphene oxide that concentration is 2.5 mg/mL and suspends
Liquid；
(2) disodium ethylene diamine tetra-acetic acid solution is stirred and is added in the graphene oxide suspension that step (1) obtains, stirred
Mix mixing；
Mixed solution the preparation method comprises the following steps: weighing 5g disodium ethylene diamine tetraacetate crystal in 250 ml beakers in the present embodiment
In, stirring after 250 ml of deionized water makes it dissolve is added and is added in the graphene oxide suspension in step (1), continues electronic
Stir 4h；
(3) chitosan is dissolved in glacial acetic acid, stirring is added in the mixed solution of step (2) after completely dissolution, and ultrasound is stirred
Uniform and stable suspension is persistently stirred to get after mixing；
Suspension is placed in the glacial acetic acid of 100mL2% the preparation method comprises the following steps: weighing 5g chitosan in the present embodiment, uses glass
Glass plate stirring stirs it after completely dissolution in the mixed solution of addition step (2), continues electric stirring after 40min is stirred by ultrasonic
16h, wherein the mass ratio of graphene oxide, disodium ethylene diamine tetraacetate and chitosan is 1:10:10；
(4) suspension in step (3) is obtained into brown product with deionized water filtering and washing afterwards for several times, it is dry is placed in vacuum
Drying to constant weight, grinding, 200 meshes excessively obtains modified graphene oxide/Chitosan Composites at 60 DEG C in dry
(GEC10)。
The preparation method of graphene oxide in the present embodiment is same as Example 1.
Microstructure, infrared spectrum analysis and the X of modified graphene oxide/Chitosan Composites manufactured in the present embodiment
Ray diffraction analysis result is similar to Example 1.
Embodiment 3
(1) graphite oxide suspension is ultrasonically treated 2 h, obtains the graphene oxide that concentration is 2.5 mg/mL and suspends
Liquid；
(2) disodium ethylene diamine tetra-acetic acid solution is stirred and is added in the graphene oxide suspension that step (1) obtains, stirred
Mix mixing；
Mixed solution burns the preparation method comprises the following steps: weighing 2.5g disodium ethylene diamine tetraacetate crystal in 250 ml in the present embodiment
In cup, stirring after 250 ml of deionized water makes it dissolve is added and is added in the graphene oxide suspension in step (1), continues electricity
Dynamic stirring 4h；
(3) chitosan is dissolved in glacial acetic acid, stirring is added in the mixed solution of step (2) after completely dissolution, and ultrasound is stirred
Uniform and stable suspension is persistently stirred to get after mixing a period of time；
Suspension is placed in the glacial acetic acid of 100mL2% the preparation method comprises the following steps: weighing 5g chitosan in the present embodiment, uses glass
Glass plate stirring stirs it after completely dissolution in the mixed solution of addition step (2), continues electric stirring after 40min is stirred by ultrasonic
16h, wherein the mass ratio of graphene oxide, disodium ethylene diamine tetraacetate and chitosan is 1:5:10；
(4) suspension in step (3) is obtained into brown product with deionized water filtering and washing afterwards for several times, it is dry is placed in vacuum
Drying to constant weight, grinding, 200 meshes excessively obtains modified graphene oxide/Chitosan Composites at 60 DEG C in dry
(GEC5)。
The preparation method of graphene oxide in the present embodiment is same as Example 1.
Microstructure, infrared spectrum analysis and the X of modified graphene oxide/Chitosan Composites manufactured in the present embodiment
Ray diffraction analysis result is similar to Example 1.
Embodiment 4
Test 1
The present invention is to modified graphene oxide/Chitosan Composites under the conditions of different adsorption times to Cr VI in solution
The adsorbance of ion compares, specific steps are as follows:
(1) stuffed conical flask that 25 ml hexavalent chromium solutions are separately added into 50 ml is drawn, then the modified oxidized stone of 0.02g
Conical flask is added in black alkene/Chitosan Composites, and then conical flask is placed in constant-temperature table；
(2) solution ph in above-mentioned conical flask be 2, constant temperature shaker temperature be set as 25 DEG C, revolving speed be set as 160
Rpm, adsorption time are respectively 1,3,5,10,20,40,60,90,120,150,180 min；
(3) each group solution is filtered with the filter membrane of 0.45um after above-mentioned adsorption process, is measured remaining in solution
The concentration of hexavalent chromium calculates adsorbance.
(4) result as shown in fig. 6, with adsorption time increase, modified graphene oxide/Chitosan Composites are to molten
The adsorbance of hexavalent chromium gradually increases in liquid, close to adsorption equilibrium when adsorption time is 60min, modified graphene oxide/
Chitosan Composites are far superior to graphene oxide/Chitosan Composites (GC) and shell to the adsorption effect of hexavalent chromium
Glycan (CS).
Test 2
The present invention is to modified graphene oxide/Chitosan Composites under the conditions of different solutions initial pH value in solution six
The adsorbance of valence chromium ion compares, specific steps are as follows:
(1) hexavalent chromium solution for drawing 25 ml difference pH value is separately added into the stuffed conical flask of 50 ml, then 0.02g
Modified graphene oxide/Chitosan Composites are added conical flask and stopper glass stopper, and conical flask is then placed in constant-temperature table
In；
(2) solution ph in above-mentioned conical flask is respectively 2,3,5,7,9,11, constant temperature shaker temperature be set as 25 DEG C,
Revolving speed is set as 160 rpm, adsorption time 60min；
(3) each group solution is filtered with the filter membrane of 0.45um after above-mentioned adsorption process, is completed six in aqueous solution
The Adsorption of valence chromium ion measures the concentration of remaining hexavalent chromium in solution, calculates adsorbance.
(4) result as shown in fig. 7, with solution ph reduction, modified graphene oxide/Chitosan Composites are to molten
The adsorbance of hexavalent chromium is gradually increased in liquid, shows that acid condition is conducive to the progress of absorption；Modified graphene oxide/shell
Polysaccharide composite material is much larger than graphene oxide/chitosan and chitosan to the adsorbance of hexavalent chromium.
Test 3
The present invention is to modified graphene oxide/suction of the Chitosan Composites difference dosage to hexavalent chromium in solution
Attached amount compares, specific steps are as follows:
(1) 50 ml are added in the hexavalent chromium solution that batch draws that 50ml initial concentration is 50 ppm, initial pH value is 2
In stuffed conical flask, appropriate adsorbent is then successively put into；
(2) above-mentioned adsorbent dosage is respectively 0.2,0.4,0.8,1.2,1.6,2.0 and 3.0 g/L, and all tools are filled in
Conical flask be uniformly placed in 25 DEG C of temperature, 160 rpm of revolving speed constant-temperature table in, shake 60min after take out；
(3) each group solution is filtered with the filter membrane of 0.45um after above-mentioned adsorption process, is completed six in aqueous solution
The Adsorption of valence chromium ion measures the concentration of remaining hexavalent chromium in solution, calculates adsorbance.
(4) result as shown in figure 8, with adsorbent dosage increase, the removal rate of hexavalent chromium is not yet in solution
Disconnected to increase, when dosage is 2.0 g/L, removal rate reaches 90% or more.
Test 4
The thermoisopleth that the present invention adsorbs modified graphene oxide/Chitosan Composites to hexavalent chromium in solution is done
Research, specific steps are as follows:
(1) the hexavalent chromium solution that batch draws that 25ml initial pH value is 2 is added in 50 ml stuffed conical flasks, then
Successively put into 0.02g adsorbent；
(2) above-mentioned initial concentration solution is respectively 20,40,50,60,80 and 100 ppm, and all stuffed conical flasks are united
One be respectively placed in 25 DEG C of temperature, 35 DEG C, 45 DEG C, in the constant-temperature table of 160 rpm of revolving speed, taken out after shaking 60min；
(3) each group solution is filtered with the filter membrane of 0.45um after above-mentioned adsorption process, is completed six in aqueous solution
The Adsorption of valence chromium ion measures the concentration of remaining hexavalent chromium in solution, calculates adsorbance.
(4) as shown in figure 9, adsorbance increases with the raising of reaction Wensu, i.e. high temperature is conducive to adsorb result, and inhales
Attached amount increases with the increase of Cr VI initial concentration.
Test 5
The present invention carries out desorption and regeneration, specific steps to modified graphene oxide/Chitosan Composites of adsorption saturation
Are as follows:
(1) sodium hydroxide solution is added into the conical flask of the adsorbent equipped with adsorption saturation, will owns after stoppering bottle stopper
Conical flask, which is uniformly placed in constant-temperature table, to be shaken；
(2) concentration of above-mentioned sodium hydroxide solution is respectively 0.1 mol/L, and constant temperature shaker temperature is 25 DEG C, revolving speed is
180 rpm, concussion time are 3 h；
(3) adsorbent in each conical flask is separated after above-mentioned desorption process from solution, then uses deionized water
Washing, 60 DEG C of dryings in drying box.
(4) the results are shown in Figure 10, it still has hexavalent chromium good after 7 wheel adsorption-desorption experiments
Adsorption capacity, adsorbance decline are only 5%, illustrate that modified graphene oxide/Chitosan Composites have good reproducibility
Can, it can be used as the excellent adsorbent of one kind and be generalized in practical application.
Claims (3)
1. a kind of preparation method of modified graphene oxide/Chitosan Composites, it is characterised in that: the ethylenediamine of water will be dissolved in
Tetraacethyl disodium stirring is added in the graphene oxide suspension obtained after ultrasonic treatment, mixes it uniformly, is subsequently agitated for adding
Enter to be dissolved in the chitosan solution in glacial acetic acid, be stirred by ultrasonic, after lasting electric stirring, through suction filtration, centrifugation, vacuum drying and
Modified graphene oxide/Chitosan Composites are obtained after being ground up, sieved；
The following steps are included:
(1) graphene oxide suspension is obtained by graphite oxide suspension is sonicated；
(2) disodium ethylene diamine tetra-acetic acid solution is stirred and is added in graphene oxide suspension obtained in step (1), stirring is mixed
It closes；
(3) chitosan is dissolved in glacial acetic acid, stirring is added in the mixed solution of step (2) after completely dissolution, after ultrasonic agitation
Persistently stir to get uniform and stable suspension；
(4) modified graphite oxide is obtained after the suspension in step (3) being filtered, be centrifuged, be dried in vacuo and be ground up, sieved
Alkene/Chitosan Composites；
Sonication treatment time described in step (1) is 1h ~ 3h, and the concentration of the graphene oxide suspension is 2.5mg/mL ~ 5
mg/mL；
In step (2), the concentration of the disodium ethylene diamine tetra-acetic acid solution is 15g/L ~ 25g/L, and the time being stirred is 4h
~6 h；
In step (3), the time of the ultrasonic agitation is 30min-60min, and the time persistently stirred is the h of 14h ~ 18；It is dissolved in ice
The mass percent concentration of the chitosan solution of acetic acid is 1% ~ 4%, and the graphene oxide, disodium ethylene diamine tetraacetate and shell are poly-
The mass ratio of sugar is 1:5 ~ 10:5 ~ 10；
The preparation of modified graphene oxide/Chitosan Composites carries out at room temperature, and vacuum drying temperature is 50 DEG C ~ 80
℃；
Modified graphene oxide/the Chitosan Composites include graphene oxide, disodium ethylene diamine tetraacetate and chitosan；
The disodium ethylene diamine tetraacetate passes through its amino by the carboxylic-bond on amino group and graphene oxide, chitosan
With hydroxyl on graphene oxide carboxyl and hydroxyl generate bonding action and be combined together with electrostatic interaction.
2. modified graphene oxide/Chitosan Composites are as adsorbent application made from preparation method described in claim 1
In the processing of heavy metal-containing waste water.
3. the application of modified graphene oxide/Chitosan Composites, feature made from preparation method described in claim 1 exist
In: the hexavalent chromium in removal heavy metal-containing waste water, the specific steps are as follows:
Every liter of chromate waste water is added 0.2 ~ 3.0 g of modified graphene oxide/Chitosan Composites, and control waste water temperature is 25 ~
It 45 DEG C, fullys shake to fully reacting, adsorbent material is separated with waste water, with the sodium hydroxide solution of 1 mol/L to absorption
The adsorbent of saturation is desorbed, and control reaction temperature is 25 DEG C, is fullyd shake, and recycles adsorbent after desorption is complete.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201510915633.XA CN105498707B (en) | 2015-12-10 | 2015-12-10 | A kind of preparation method and application of modified graphene oxide/Chitosan Composites |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201510915633.XA CN105498707B (en) | 2015-12-10 | 2015-12-10 | A kind of preparation method and application of modified graphene oxide/Chitosan Composites |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN105498707A CN105498707A (en) | 2016-04-20 |
| CN105498707B true CN105498707B (en) | 2019-03-05 |
Family
ID=55707240
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201510915633.XA Expired - Fee Related CN105498707B (en) | 2015-12-10 | 2015-12-10 | A kind of preparation method and application of modified graphene oxide/Chitosan Composites |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN105498707B (en) |
Families Citing this family (14)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106944006A (en) * | 2017-03-30 | 2017-07-14 | 山东金利特新材料有限责任公司 | A kind of preparation method and application of modified graphene oxide/Chitosan Composites |
| CN108732216B (en) * | 2017-04-19 | 2020-08-18 | 北京信息科技大学 | Electrochemical reduction graphene oxide modified electrode and application thereof in detection of heavy metal hexavalent chromium ions in water |
| US20190110963A1 (en) * | 2017-10-18 | 2019-04-18 | Northwestern University | Graphene-based multifunctional cosmetic compositions |
| CN108295812B (en) * | 2018-03-14 | 2021-02-12 | 河南城建学院 | Graphene oxide composite membrane for selectively removing metal ions in water, and preparation method and application thereof |
| CN109319895B (en) * | 2018-10-23 | 2021-10-08 | 四川意德康环保科技有限公司 | Nano chitosan modified polyaluminum chloride and preparation method thereof |
| CN109626731A (en) * | 2018-12-28 | 2019-04-16 | 成都硕特环保科技有限公司 | The method of inorganic salts is recycled from high saliferous modified starch waste water |
| CN109806845A (en) * | 2019-03-20 | 2019-05-28 | 上海应用技术大学 | Chitosan/magnesium hydroxide/reduced graphene gel adsorption material and preparation |
| CN113652237B (en) * | 2021-06-24 | 2022-08-26 | 天津华勘环保科技有限公司 | Green eluting agent for heavy metal/organic matter composite contaminated soil remediation and use method thereof |
| CN113318710A (en) * | 2021-07-07 | 2021-08-31 | 长春工业大学 | Preparation method of graphene oxide/chitosan composite material adsorbent |
| CN113509909A (en) * | 2021-07-22 | 2021-10-19 | 南京和于润科技有限公司 | Water pollution remediation agent and preparation method thereof |
| CN113603895B (en) * | 2021-08-16 | 2022-03-29 | 南京工业大学 | Preparation method of chitosan-graphene oxide hybrid material |
| CN114213719B (en) * | 2021-11-10 | 2023-03-17 | 河北科技师范学院 | Preparation method and application of sulfonated graphene oxide-chitosan composite material |
| CN114213718B (en) * | 2021-11-10 | 2023-03-28 | 河北科技师范学院 | Preparation method and application of chitosan oxide-graphene oxide composite material |
| CN114668074B (en) * | 2022-04-18 | 2024-01-26 | 成都蜀星饲料有限公司 | Feed additive and preparation method thereof |
Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN103447013A (en) * | 2013-09-23 | 2013-12-18 | 青岛大学 | Method for preparing graphene/chitosan adsorbent and application method thereof |
Family Cites Families (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR101286235B1 (en) * | 2011-12-27 | 2013-07-15 | 한국과학기술연구원 | Apparatus and method for fabricating antimicrobial hybrid materials of natural product and carbon nanomaterials |
-
2015
- 2015-12-10 CN CN201510915633.XA patent/CN105498707B/en not_active Expired - Fee Related
Patent Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN103447013A (en) * | 2013-09-23 | 2013-12-18 | 青岛大学 | Method for preparing graphene/chitosan adsorbent and application method thereof |
Non-Patent Citations (3)
| Title |
|---|
| EDTA functionalized magnetic grapheme oxide for removal of Pb(II),Hg(II) and Cu(II) in water treatment: Adsorption mechanism and separation property;Limei Cui, et al;《Chemical Engineering Journal》;20150625;第281卷;第2页左栏最后1段至右栏第3段 |
| Enhanced mechanical properties of chitosan/EDTA-GO nanocomposites thin films;N. I. Syuhada, et al;《Sains Malaysiana》;20141231;第43卷(第6期);第851页右栏最后1段至第852页右栏第2段、第857页图2 |
| Microwave preparation of triethylenetetramine modified grapheneoxide/chitosan composite for adsorption of Cr(VI);Huacai Ge, et al;《Carbohydrate Polymers》;20150616;第131卷;第280-287页 |
Also Published As
| Publication number | Publication date |
|---|---|
| CN105498707A (en) | 2016-04-20 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN105498707B (en) | A kind of preparation method and application of modified graphene oxide/Chitosan Composites | |
| CN104772113B (en) | A kind of graphene/montmorillonite nano-composite material and preparation method and application | |
| CN107282025B (en) | Nano-cellulose base is functionalized the preparation method of aerogel type heavy-metal adsorption material | |
| CN111229157B (en) | Preparation method of inorganic polymer modified bentonite adsorption material | |
| CN105622960B (en) | A kind of carboxymethyl chitosan/oxidized graphene composite aquogel and its preparation and application | |
| CN106000311A (en) | Biological charcoal loaded with iron/zinc nano-particles as well as preparation method and application thereof | |
| CN108176373A (en) | A kind of graphene oxide corn straw modification charcoal and preparation method thereof and in sewage is removed heavy metal application | |
| CN109261133A (en) | A kind of ferromagnetism composite balls and its application being easily recycled | |
| CN111068632A (en) | Lead ion composite adsorbent and preparation method thereof | |
| CN105688837A (en) | Nanofiber membrane for removing cadmium and arsenical from water and preparation method of nanofiber memebrane | |
| CN107081123A (en) | Magnetic magnesium hydroxide adsorbent and preparation method thereof | |
| Yang et al. | Capturing lithium using functional macroporous microspheres with multiple chambers from one-step double emulsion via a tailoring supramolecular route and postsynthetic interface modification | |
| CN104587956A (en) | Preparation method of coated nano zero-valent iron taking multilayer activated-carbon-coated graphene oxide composite powder as carrier | |
| CN104492391B (en) | A kind of preparation method of chitosan-modified albumin nanospheres heavy-metal adsorption material | |
| CN106390940A (en) | Modified bio-char as well as preparation method and application thereof | |
| CN107519846A (en) | A kind of graphene/silicon dioxide Pt/Polypyrrole composite material and preparation method and application | |
| CN105854787A (en) | Preparation method for quaternary ammonium salt modified attapulgite for heavy metal adsorption | |
| CN111018037B (en) | Method for removing heavy metal mercury ions in water based on polyacrylonitrile nano-film compound | |
| CN109499393A (en) | A kind of super hydrophilic PVDF water-oil separationg film and the preparation method and application thereof separating oily wastewater | |
| CN107008230A (en) | Magnetic composite adsorbent and preparation method thereof | |
| CN109876780A (en) | A kind of dephosphorization adsorbent and preparation method thereof | |
| Wang et al. | Preparation of egg white@ zeolitic imidazolate framework-8@ polyacrylic acid aerogel and its adsorption properties for organic dyes | |
| CN108295812A (en) | A kind of graphene oxide composite membrane for selective removal underwater gold category ion and preparation method thereof, application | |
| CN106268673B (en) | A kind of preparation method of amino modified chitosan composite adsorbing material | |
| CN104289200B (en) | A kind of preparation method and application of magnetic HACC/ oxidation multi-walled carbon nano-tubes adsorbent |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C06 | Publication | ||
| PB01 | Publication | ||
| C10 | Entry into substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| GR01 | Patent grant | ||
| GR01 | Patent grant | ||
| CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20190305 |